Physical-chemical characterization of pig slurry at each stage of the treatment system.

Physical-chemical characterization of pig slurry at each stage of the treatment system.

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The main objective of this study was to analyze the efficiency of CWs for purifying swine wastewater in order to reduce its pollutant load. The system included a pretreatment module (raw swine wastewater tank, phase separator, and settlement tank), and three constructed wetlands connected in series and planted with Phragmites australis and Suaeda v...

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... analyses were performed using SPSS (SPSS Version 23.0, Chicago, IL, USA). Table 1 shows the characterization of slurry at each stage of the treatment system. As can be seen, after the phase separator, the temperature showed no significant differences with respect to the raw slurry, with a value of 12.9 ± 1.6 • C in the storage tank. ...
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... swine wastewater pH had a slight non-significant increase after the phase separator (Table 1). The mean pH values were slightly alkaline, showing almost identical values of around eight at the end of the CWs; oppositely, Schierano et al. [21] found a reduction in pH values (from 8.55-9.25 to 7.95-8.75) ...
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... the observed decrease was only significant for PC3, which could be due to a release of ions from the CWs caused by the interaction between the substrate and the biofilm within the wetland [4]. The anions showed no significant differences between the PB and the resulting slurry in PC3, except for PO 4 3− , NO 3 − , and SO 4 2− , which decreased from 147 ± 39.7 mg L −1 to 35.4 ± 4.3 mg L −1 for PO 4 3− , whilst increasing significantly for SO 4 2− and NO 3 − ( Table 1). The cations also showed no statistically significant differences, except for K+, with concentrations of 787 ± 25.9 mg L −1 for raw slurry and 312 ± 22.3 mg L −1 for slurry after passing through the CWs. ...
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... should be noted that the minus sign means that the parameter increased with respect to the initial value (Table 2). The pH varied from 7.8 in the influent to 7.8 in the effluent of the CW (Table 1), without a statistical difference. In the case of the EC, the phase separator decreased its value by 25%, whilst the wetland also enabled us to reduce the EC by 25%, with a total reduction of 44%. ...
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... from the atmosphere together with the release of oxygen from the rhizosphere would favor nitrification processes, whilst anaerobic conditions in the lower part of the CWs would favor denitrification [35]. The behavior of the anions was very heterogeneous, with extremely high values being obtained, especially in the cases of N-NO 2 − , N-NO 3 − , and SO 4 2− , with a total increase in the N-NO 2 − , N-NO 3 − , and SO 4 2 concentrations from 0.03 to 1.6 mg L −1 , from 7,5 to 100 mg L −1 , and from 152 to 1514 mg L −1 , respectively (Table 1). The cations increased as they passed through the system, showing negative total efficiencies, except for K + with a total efficiency of 60%; this was due to the release of cations, especially of calcium and magnesium, from the calcareous substrate used in constructing the wetland. ...

Citations

... These technologies are classified into three categories: physical, chemical, and biological. Physico-chemical methods, such as coagulation and crystallization, are effective in separating and precipitating contaminants, as well as recovering nutrients from slurry (Chen et al., 2024;García-Valero et al., 2024). Among the biological processes, anaerobic digestion and composting stand out for their ability to transform organic waste into biogas and generate digestate, a biofertilizer rich in N, P, and K, used in agriculture (Meng et al., 2023;Montalvo et al., 2020). ...
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... The TW cells were filled with two types of substrates, boleo with diameter between 5 and 7 ′′ , a constant layer thickness 40 cm high in all areas, filled with crushed gravel with diameters between ½ ′′ to 1 ½ ′′ and 15 cm before the top edge of each wall. The first layer had a porosity of 8% and the second layer had a porosity of 35%, with a total layer porosity of 43% ( Figure 2) to promote anaerobic conditions [27,28]. All systems had 3 days of HRT. ...
... The TW cells were filled with two types of substrates, boleo with diameter between 5 and 7″, a constant layer thickness 40 cm high in all areas, filled with crushed gravel with diameters between ½″ to 1 ½″ and 15 cm before the top edge of each wall. The first layer had a porosity of 8% and the second layer had a porosity of 35%, with a total layer porosity of 43% ( Figure 2) to promote anaerobic conditions [27,28]. All systems had 3 days of HRT. ...
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